Principles of terrestrial ecosystem ecology.pdf
Principles of terrestrial ecosystem ecology.pdf
Principles of terrestrial ecosystem ecology.pdf
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Figure 6.9. Representative seasonal pattern <strong>of</strong> gross<br />
primary production, <strong>ecosystem</strong> respiration, and net<br />
<strong>ecosystem</strong> production <strong>of</strong> an <strong>ecosystem</strong>. NEP is the<br />
difference between two large fluxes (carbon inputs<br />
in GPP and carbon losses, <strong>of</strong> which R ecosyst and Fleach<br />
are generally greatest).Annual CO2 flux in this graph<br />
is at steady state because the NEP summed over the<br />
annual cycle is close to zero. Here, carbon losses due<br />
to disturbance are assumed to be zero.<br />
released to the atmosphere (see Chapter 10).<br />
Approximately 20% <strong>of</strong> the CO 2 produced in<br />
arctic soils, for example, leaches to groundwater<br />
and is released from lakes and streams<br />
(Kling et al. 1991). Dissolved organic carbon<br />
is also lost from <strong>ecosystem</strong>s by leaching to<br />
groundwater. Despite their importance, leaching<br />
losses <strong>of</strong> carbon to groundwater are seldom<br />
measured and therefore frequently ignored in<br />
<strong>ecosystem</strong> carbon budgets.<br />
Lateral Transfers<br />
Lateral transfer <strong>of</strong> carbon into or out <strong>of</strong> <strong>ecosystem</strong>s<br />
can be important to the long-term carbon<br />
budgets <strong>of</strong> <strong>ecosystem</strong>s. Carbon can move laterally<br />
in <strong>ecosystem</strong>s through erosion and deposition<br />
by wind or water or by movement by<br />
animals (Fig. 6.8). These lateral transfers are<br />
usually so small that they are undetectable in<br />
any single year. Over long time periods or<br />
during extreme events, such as floods or landslides,<br />
these lateral transfers can, however, be<br />
quantitatively important. These transfers are<br />
typically more important for elements that are<br />
tightly cycled within <strong>ecosystem</strong>s and have small<br />
annual inputs and losses (e.g., phosphorus) than<br />
they are for carbon.<br />
Disturbance<br />
Net Ecosystem Production 145<br />
Disturbance is an episodic cause <strong>of</strong> carbon loss<br />
from many <strong>ecosystem</strong>s. Disturbances such as<br />
fire and harvest <strong>of</strong> plants or peat can be the<br />
dominant avenues <strong>of</strong> carbon losses from <strong>ecosystem</strong>s<br />
in the years when they occur. In many<br />
cases the carbon losses with disturbance are so<br />
large that they become significant components<br />
<strong>of</strong> long-term carbon budgets (Fig. 6.8; Box 6.1).<br />
Carbon losses during fires in the Canadian<br />
boreal forest, for example, are equivalent to 10<br />
to 30% <strong>of</strong> average NPP (Harden et al. 2000).<br />
Controls over Net<br />
Ecosystem Production<br />
NEP is determined by factors that cause an<br />
imbalance between carbon gain and loss. An<br />
<strong>ecosystem</strong> is never at equilibrium at any<br />
moment in time. NEP varies with season, time<br />
since disturbance, interannual variation in<br />
weather, and long-term trends in environment.<br />
High-latitude <strong>ecosystem</strong>s, for example, are a net<br />
carbon source in warm years and a carbon sink<br />
in cool years (Goulden et al. 1998) because heterotrophic<br />
respiration responds to temperature<br />
more strongly than does photosynthesis in cold<br />
climates. We expect NEP to change in response<br />
to long-term changes in any factor that differs in<br />
its effects on GPP and the various avenues <strong>of</strong><br />
carbon loss from <strong>ecosystem</strong>s (e.g., plant respiration,<br />
heterotrophic respiration, disturbance,<br />
or leaching loss). Increased concentrations <strong>of</strong><br />
atmospheric CO2 or nitrogen inputs to <strong>ecosystem</strong>s,<br />
for example, have greater direct effects on<br />
GPP than on decomposition, whereas a reduction<br />
in the soil moisture <strong>of</strong> poorly drained<br />
wetlands increases decomposition and fire<br />
probability more strongly than it affects NPP.<br />
Human activities are currently having greatest<br />
impact on precisely those environmental factors<br />
that we expect to affect plants and decomposers<br />
differentially and therefore to affect global <strong>terrestrial</strong><br />
carbon storage (see Chapter 15).<br />
Net carbon accumulation by an <strong>ecosystem</strong><br />
depends more strongly on time since disturbance<br />
than on climate. The greatest causes <strong>of</strong><br />
variation in NEP among <strong>ecosystem</strong>s are cycles